Appendix S1.
Full description of the eastern chestnut mouse and co-occurring small mammal species.
Eastern chestnut mouse ( Pseudomys gracilicaudatus )
The eastern chestnut mouse is an endemic Australian murid rodent. It has a disjunct distribution along the east coast of Australia (inset Fig. 2) and is absent throughout much of its range. The Jervis Bay region supports the most southerly contemporary population of the species (Meek and Triggs 1997). Usually reported at low density, the eastern chestnut mouse has been recorded in grassy open woodland to open dry sclerophyll forest, but is more often found in heathland (Fox 2008) where populations peak in abundance post-fire before declining over time as vegetation regenerates (Fox
1982). Threats to the viability of populations of this species’ are thought to include fire suppression, loss of heath habitat, and predation (Fox 2008).
The eastern chestnut mouse is an annual summer breeder capable of producing multiple litters of one to five (usually three) offspring (Fox 2008). Early development is rapid which contrasts with a slow growth rate to reach maturity (Fox & Kemper
1982). Adults show significant sexual dimorphism (Fox & Kemper 1982) and attain average weights of 90 g for males and 75 g for females (Fox 2008). The species’ lifespan is less than two years in wild populations (Watts & Kemper 1989). Studies of the eastern chestnut mouse dietary requirements indicate it is a generalist herbivore, opportunistic in foraging and less specialised in food selection than any other species within the genus (Luo et al. 1994). The eastern chestnut mouse is terrestrial, mostly nocturnal, and individuals select diurnal refuges associated with the presence of specific structures including grass trees ( Xanthorrhea spp.), buttongrass

( Gymnoschoenus sp.), collapsed dead stems, and areas of tall, dense vegetation
(Pereoglou et al. 2011). The eastern chestnut mouse is transient and non-gregarious in its use of shelter sites (Pereoglou et al. 2011). Little is known about social organisation and behaviour. Radio-tracking data suggests that adults of the eastern chestnut mouse are solitary and territorial, with females having a home range of 0.5 –
1 ha and up to 4 ha for males (Pereoglou et al . unpublished data).
Bus rat ( Rattus fuscipes )
The bush rat is a common and widespread terrestrial murid rodent that occurs throughout many parts of eastern Australia (Watts & Aslin 1981). The species can be found in many different habitats and is widespread in eucalypt forest and areas where there is a dense understory (Breed and Ford 2007). Weights in excess of 200 g have been recorded for adult animals (Lunney 2008a). Bush rats are capable of breeding all year round under favourable (wet) conditions, but births predominantly occur in late spring and summer with litter size ranging from one to seven (average five) (Watts and Aslin 1981). Multiple litters can be produced in the breeding season, with animals born early attaining sexual maturity in the same season, and all animals capable of breeding in the following spring (Watts and Aslin 1981). Mortality occurs after breeding and the average lifespan of most animals is one year (Watts and Aslin 1981); few individuals (< 5%) survive to breed a second year (Robinson 1987). The bush rat has an omnivorous diet of fungi, seeds, fruit, plant tissue and arthropods (Warneke
1971). The species is nocturnal but not strictly territorial; home ranges can overlap
(Lunney 2008a) with male territories being larger than those of females (Watts and
Aslin 1981).

Swamp rat ( R. lutreolus )
The swamp rat is a native murid rodent distributed over coastal and sub-coastal southeastern Australia (Lunney 2008b). The species occurs predominantly in heathland and sedgeland (Braithwaite 1982), and prefers areas of wet, dense cover (Lunney 2008b).
Adult animals attain an average weight of approximately 200 g (Lunney 2008b).
Breeding occurs in summer (Watts and Aslin 1981). Like its congener, the bush rat, the swamp rat is capable of breeding year around provided conditions are favourable.
Females can produce multiple litters of three to five young in a single season, and offspring born early are able to breed in the season of their birth (Lunney 2008b).
Longevity is also probably similar to the bush rat, being mostly annual. The swamp rat is a specialist herbivore whose main diet consists of grasses and sedges (Watts and
Aslin 1981). The species shelters in burrows or builds above-ground nests in waterlogged areas (Lunney 2008b). The swamp rat is partially diurnal and moves through runways constructed in dense vegetation (Watts and Aslin 1981). Male home ranges are larger than non-overlapping female ranges, and individuals exhibit territorial social behaviour throughout much of the year (Lunney 2008b). The swamp rat is immediately and adversely affected by fire due to the species’ dependence on dense cover (Lunney 2008b) and relatively specialised diet (Braithwaite 1982).
Brown antechinus ( Antechinus stuartii )
The brown antechinus is a small dasyurid marsupial, widespread in forest and heathland throughout its coastal distribution from southern Queensland to southern
New South Wales, Australia (Crowther 2002). The brown antechinus is mostly terrestrial although it also can be arboreal depending on the habitat. High density populations are found in areas with thick ground cover and abundant logs (Crowther

and Braithwaite 2008). Adult males and females attain average weights of 35 g and 20 g, respectively. Mating occurs in winter, and females typically have 8 – 10 pouch young. Multiple paternity is common (Kraaijeveld-Smit et al. 2002), with most litters being sired by two or three males. All males die at the end of a two-week mating season, although some females may survive to breed in a second year (Crowther and
Braithwaite 2008). The brown antechinus is an opportunistic insectivore (Fox and
Archer 1984). Ranging behaviour is probably similar to the agile antechinus ( A. agilis ), with males covering an area three times greater than that of females (Dickman
2008). Individuals nest communally, usually in hollow logs of tree trunks. Malebiased post-natal dispersal occurs in summer and individuals may continue to move between communal nests prior to the breeding season (Cockburn and Lazenby-Cohen
1992).
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